Levels, distribution, and health risk of phthalate esters in urban soils of Beijing, China.

The content of phthalate esters (PAEs) was investigated in urban soil samples ( = 127, 0-20 cm) collected from a business area (BU), classical garden (CL), culture and educational area (CU), large public green space (LA), residential area (RE), and roadside area (RO) in Beijing. The sum of all PAE contents ranged from 1.9 to 3141.7 ng/g, with an average of 1139.6 ± 727.6 ng/g. Di-n-butyl phthalate (DBP) and di-(2-ethylhexyl) phthalate (DEHP) were the major contaminants in the soil samples. The content of DEHP and DBP in the urban soil of Beijing showed decreasing trends from the center of the city to the suburbs, which was probably because the center of the city has a longer history. In addition, higher DBP content also occurred in the south of the city, which was caused by the existence of several factories that produce commodity chemical and building materials in these areas. Because of its greater age, less disturbance from human activity, and high levels of total organic carbon and black carbon in CL, PAE content in CL was the highest among the six types of land use, followed by RE, CU, BU, LA, and RO. Although in 82.6% of the soil samples, DBP content exceeded the recommended allowable soil content in New York, USA, health risk assessment with CalTOX and Monte Carlo analysis showed that the total cancer risk values of PAEs were lower than the acceptable cancer risk value (10(-4)) and that the risk mainly came from dermal uptake and inhalation exposure pathways.

[1]  T. Bucheli,et al.  Is black carbon a better predictor of polycyclic aromatic hydrocarbon distribution in soils than total organic carbon? , 2011, Environmental pollution.

[2]  Chi Sun Poon,et al.  Heavy metal contamination of urban soils and street dusts in Hong Kong , 2001 .

[3]  X. Xia,et al.  Mercury in urban soils with various types of land use in Beijing, China. , 2010, Environmental pollution.

[4]  L. Yun,et al.  The study of PAEs in soils from typical vegetable fields in areas of Guangzhou and Shenzhen, South China , 2005 .

[5]  J. Rouzaud,et al.  Evaluation of a protocol for the quantification of black carbon in sediments , 2001 .

[6]  X. Li,et al.  Phthalate Ester Pollution in Urban Soil of Beijing, People's Republic of China , 2006, Bulletin of environmental contamination and toxicology.

[7]  Hwong-wen Ma,et al.  Model comparison for risk assessment: a case study of contaminated groundwater. , 2006, Chemosphere.

[8]  Shaoda Liu,et al.  Distribution and sources of DDTs in urban soils with six types of land use in Beijing, China. , 2010, Journal of hazardous materials.

[9]  L. Carlsen,et al.  Phthalates and nonylphenols in profiles of differently dressed soils. , 2002, The Science of the total environment.

[10]  C. Fan,et al.  Atmospheric distribution of particulate- and gas-phase phthalic esters (PAEs) in a Metropolitan City, Nanjing, East China. , 2008, Chemosphere.

[11]  P. Abrahams Soils: their implications to human health. , 2002, The Science of the total environment.

[12]  Min Liu,et al.  Phthalate esters (PAEs): emerging organic contaminants in agricultural soils in peri-urban areas around Guangzhou, China. , 2008, Environmental pollution.

[13]  R. H. Mckee,et al.  NTP center for the evaluation of risks to human reproduction reports on phthalates: addressing the data gaps. , 2004, Reproductive toxicology.

[14]  X. Shan,et al.  Survey of phthalate pollution in arable soils in China. , 2003, Journal of environmental monitoring : JEM.

[15]  L. Ma,et al.  Organic contamination in the greenhouse soils from Beijing suburbs, China. , 2003, Journal of environmental monitoring : JEM.

[16]  A. Beck,et al.  Analysis of 4-nonylphenols, phthalates, and polychlorinated biphenyls in soils and biosolids. , 2005, Chemosphere.

[17]  E. Zeng,et al.  Strong sorption of phenanthrene by condensed organic matter in soils and sediments. , 2007, Environmental science & technology.

[18]  Min Liu,et al.  Distribution of phthalate esters in urban soils of subtropical city, Guangzhou, China. , 2009, Journal of hazardous materials.

[19]  P. Gschwend,et al.  Quantification of the dilute sedimentary soot phase : Implications for PAH speciation and bioavailability , 1997 .

[20]  J. Grimalt,et al.  Temperature and organic matter dependence of the distribution of organochlorine compounds in mountain soils from the subtropical Atlantic (Teide, Tenerife Island). , 2002, Environmental science & technology.

[21]  Z. Vryzas,et al.  Determination of triazine and chloroacetanilide herbicides in soils by microwave-assisted extraction (MAE) coupled to gas chromatographic analysis with either GC-NPD or GC-MS. , 2002, Journal of agricultural and food chemistry.

[22]  M. Blanchard,et al.  Atmospheric fate of phthalate esters in an urban area (Paris-France). , 2006, The Science of the total environment.

[23]  Jaap Struijs,et al.  Occurrence of phthalate esters in the environment of The Netherlands. , 2006, Ecotoxicology and environmental safety.

[24]  F. Gobas,et al.  Sorption of phthalate esters and PCBs in a marine ecosystem. , 2006, Environmental science & technology.

[25]  Jiping Zhu,et al.  Phthalate esters in human milk: concentration variations over a 6-month postpartum time. , 2006, Environmental science & technology.